|
ACTIVITIES IMPLEMENTED JOINTLY (AIJ)
List of Projects
USIJI Uniform Reporting Document:
Activities Implemented Jointly Under the Pilot Phase
A. Description of the AIJ project
1. Title of project: Rio Bravo Carbon Sequestration Pilot Project
2. Host country: Belize
3. Brief project description:
- The Rio Bravo Carbon Sequestration Pilot Project is a forestry project located in northwest Belize, within the
Rio Bravo Conservation and Management Area (RBCMA). The project combines land acquisition and a sustainable
forestry program to achieve greenhouse gas (GHG) benefits from forest growth (i.e., carbon sequestration) that
would not have occurred in the absence of project activities. The objective of the project is to demonstrate an
optimal balance between cost-effective carbon sequestration, economically sustainable forest yield, and
environmental protection.
4. Participants:
|
Name of Organization or Individual
|
Country
|
|
Programme for Belize (PfB)
|
Belize
|
|
The Nature Conservancy (TNC)
|
U.S.A.
|
|
Winrock International
|
U.S.A.
|
|
Wisconsin Electric Power Company (WEPCO)
|
U.S.A.
|
|
The Detroit Edison Company
|
U.S.A.
|
|
Cinergy Services Inc.
|
U.S.A.
|
|
PacifiCorp
|
U.S.A.
|
|
UtiliTree Carbon Company
|
U.S.A.
|
|
Suncor Energy, Inc.
|
Canada
|
|
Item
|
|
|
Organization
|
|
Name of organization (original language)
or
Name of individual if unaffiliated with any organization
|
Programme for Belize
|
|
Name of organization (English)
|
(Same as above)
|
|
Acronym (original language)
|
PfB
|
|
Acronym (English)
|
(Same as above)
|
|
Department
|
|
|
Function(s) within the AIJ project activities
|
Project development, project administration
|
|
Street
|
P.O. Box 749
|
|
City
|
Belize City
|
|
State
|
|
|
Post code
|
|
|
Country
|
Belize
|
|
Telephone
|
501-2-75616 (or -617)
|
|
Fax
|
501-2-75635
|
|
E-mail
|
pfbel@btl.net
|
|
World Wide Web-URL address
|
http://www.pfbelize.org
|
|
Administrative Officer Responsible for the Project
|
|
Surname
|
Grant
|
|
First name, middle name
|
A. Joy
|
|
Job title
|
Executive Director
|
|
Direct telephone
|
501-2-75616 (or -617)
|
|
Direct fax
|
501-2-75635
|
|
Direct e-mail
|
pfbel@btl.net
|
|
Contact Person for AIJ Activities (if different from the Administrative Officer)
|
|
Surname
|
Palacio
|
|
First name, middle name
|
Vincent
|
|
Job title
|
Technical Coordinator
|
|
Direct telephone
|
501-2-75616 (or -617)
|
|
Direct fax
|
501-2-75635
|
|
Direct e-mail
|
Pfbel@btl.net
|
|
Item
|
|
|
Organization
|
|
Name of organization (original language)
or
Name of individual if unaffiliated with any organization
|
The Nature Conservancy
|
|
Name of organization (English)
|
(Same as above)
|
|
Acronym (original language)
|
TNC
|
|
Acronym (English)
|
(Same as above)
|
|
Department
|
|
|
Function(s) within the AIJ project activities
|
Project development, financing, technical assistance
|
|
Street
|
4245 N. Fairfax Drive, Suite 100
|
|
City
|
Arlington
|
|
State
|
Virginia
|
|
Post code
|
22203-1606
|
|
Country
|
U.S.A.
|
|
Telephone
|
703-841-5300
|
|
Fax
|
|
|
E-mail
|
|
|
World Wide Web-URL address
|
http://www.tnc.org
|
|
Administrative Officer Responsible for the Project
|
|
Surname
|
Sawhill
|
|
First name, middle name
|
John C.
|
|
Job title
|
President and CEO
|
|
Direct telephone
|
|
|
Direct fax
|
|
|
Direct e-mail
|
|
|
Contact Person for AIJ Activities (if different from the Administrative Officer)
|
|
Surname
|
Firstenberg
|
|
First name, middle name
|
Eric
|
|
Job title
|
Project Liaison
|
|
Direct telephone
|
703-841-2038
|
|
Direct fax
|
703-841-4880
|
|
Direct e-mail
|
efir@tnc.org
|
|
Item
|
|
|
Organization
|
|
Name of organization (original language)
or
Name of individual if unaffiliated with any organization
|
Winrock International Institute for Agricultural Development
|
|
Name of organization (English)
|
(Same as above)
|
|
Acronym (original language)
|
Winrock International
|
|
Acronym (English)
|
(Same as above)
|
|
Department
|
|
|
Function(s) within the AIJ project activities
|
Monitoring and internal verification
|
|
Street
|
38 Winrock Drive
|
|
City
|
Morrilton
|
|
State
|
Arkansas
|
|
Post code
|
72110-9370
|
|
Country
|
U.S.A.
|
|
Telephone
|
501-727-5435
|
|
Fax
|
501-727-5417
|
|
E-mail
|
|
|
World Wide Web-URL address
|
|
|
Administrative Officer Responsible for the Project
|
|
Surname
|
Brown
|
|
First name, middle name
|
Sandra
|
|
Job title
|
|
|
Direct telephone
|
541-753-5133
|
|
Direct fax
|
541-753-5131
|
|
Direct e-mail
|
sbrown@winrock.org
|
|
Contact Person for AIJ Activities (if different from the Administrative Officer)
|
|
Surname
|
|
|
First name, middle name
|
|
|
Job title
|
|
|
Direct telephone
|
|
|
Direct fax
|
|
|
Direct e-mail
|
|
|
Item
|
|
|
Organization
|
|
Name of organization (original language)
or
Name of individual if unaffiliated with any organization
|
Wisconsin Electric Power Company
|
|
Name of organization (English)
|
(Same as above)
|
|
Acronym (original language)
|
WEPCO
|
|
Acronym (English)
|
(Same as above)
|
|
Department
|
|
|
Function(s) within the AIJ project activities
|
Project development, financing
|
|
Street
|
333 Everett Street
|
|
City
|
Milwaukee
|
|
State
|
Wisconsin
|
|
Post code
|
53203
|
|
Country
|
U.S.A.
|
|
Telephone
|
|
|
Fax
|
|
|
E-mail
|
|
|
World Wide Web-URL address
|
|
|
Administrative Officer Responsible for the Project
|
|
Surname
|
|
|
First name, middle name
|
|
|
Job title
|
|
|
Direct telephone
|
|
|
Direct fax
|
|
|
Direct e-mail
|
|
|
Contact Person for AIJ Activities (if different from the Administrative Officer)
|
|
Surname
|
Cutright
|
|
First name, middle name
|
Noel
|
|
Job title
|
Senior Terrestrial Ecologist, Environmental Services
|
|
Direct telephone
|
414-221-2179
|
|
Direct fax
|
414-221-2169
|
|
Direct e-mail
|
noel.cutright@wepco.com
|
|
Item
|
|
|
Organization
|
|
Name of organization (original language)
or
Name of individual if unaffiliated with any organization
|
The Detroit Edison Company
|
|
Name of organization (English)
|
(Same as above)
|
|
Acronym (original language)
|
None
|
|
Acronym (English)
|
None
|
|
Department
|
|
|
Function(s) within the AIJ project activities
|
Financing
|
|
Street
|
2000 Second Avenue, #1051WCB
|
|
City
|
Detroit
|
|
State
|
MI
|
|
Post code
|
48226
|
|
Country
|
U.S.A.
|
|
Telephone
|
|
|
Fax
|
|
|
E-mail
|
|
|
World Wide Web-URL address
|
|
|
Administrative Officer Responsible for the Project
|
|
Surname
|
|
|
First name, middle name
|
|
|
Job title
|
|
|
Direct telephone
|
|
|
Direct fax
|
|
|
Direct e-mail
|
|
|
Contact Person for AIJ Activities (if different from the Administrative Officer)
|
|
Surname
|
DuBay
|
|
First name, middle name
|
Jim
|
|
Job title
|
Director, Environmental Initiatives
|
|
Direct telephone
|
313-235-8461
|
|
Direct fax
|
313-235-0285
|
|
Direct e-mail
|
dubayj@detroitedison.com
|
|
Item
|
|
|
Organization
|
|
Name of organization (original language)
or
Name of individual if unaffiliated with any organization
|
Cinergy Services, Inc.
|
|
Name of organization (English)
|
(Same as above)
|
|
Acronym (original language)
|
None
|
|
Acronym (English)
|
None
|
|
Department
|
|
|
Function(s) within the AIJ project activities
|
Financing
|
|
Street
|
139 E. Fourth Street, Room 552-A
|
|
City
|
Cincinnati
|
|
State
|
Ohio
|
|
Post code
|
45202
|
|
Country
|
U.S.A.
|
|
Telephone
|
|
|
Fax
|
|
|
E-mail
|
|
|
World Wide Web-URL address
|
|
|
Administrative Officer Responsible for the Project
|
|
Surname
|
|
|
First name, middle name
|
|
|
Job title
|
|
|
Direct telephone
|
|
|
Direct fax
|
|
|
Direct e-mail
|
|
|
Contact Person for AIJ Activities (if different from the Administrative Officer)
|
|
Surname
|
Kuhn
|
|
First name, middle name
|
Eric C.
|
|
Job title
|
Senior Environmental Specialist
|
|
Direct telephone
|
513-287-4061
|
|
Direct fax
|
513-287-3499
|
|
Direct e-mail
|
ekuhn@cinergy.com
|
|
Item
|
|
|
Organization
|
|
Name of organization (original language)
or
Name of individual if unaffiliated with any organization
|
PacifiCorp
|
|
Name of organization (English)
|
(Same as above)
|
|
Acronym (original language)
|
None
|
|
Acronym (English)
|
None
|
|
Department
|
|
|
Function(s) within the AIJ project activities
|
Financing
|
|
Street
|
825 NE Multomah, Suite 2000
|
|
City
|
Portland
|
|
State
|
Oregon
|
|
Post code
|
97232-2155
|
|
Country
|
U.S.A.
|
|
Telephone
|
|
|
Fax
|
|
|
E-mail
|
|
|
World Wide Web-URL address
|
|
|
Administrative Officer Responsible for the Project
|
|
Surname
|
|
|
First name, middle name
|
|
|
Job title
|
|
|
Direct telephone
|
|
|
Direct fax
|
|
|
Direct e-mail
|
|
|
Contact Person for AIJ Activities (if different from the Administrative Officer)
|
|
Surname
|
Edmonds
|
|
First name, middle name
|
Bill
|
|
Job title
|
Manager of Environmental Policy
|
|
Direct telephone
|
503-813-5291
|
|
Direct fax
|
503-813-5272
|
|
Direct e-mail
|
bill.edmonds@pacificorp.com
|
|
Item
|
|
|
Organization
|
|
Name of organization (original language)
or
Name of individual if unaffiliated with any organization
|
UtiliTree
|
|
Name of organization (English)
|
(Same as above)
|
|
Acronym (original language)
|
None
|
|
Acronym (English)
|
None
|
|
Department
|
|
|
Function(s) within the AIJ project activities
|
Financing
|
|
Street
|
c/o American Electric Power, Land Management Department
59 West Main St.
|
|
City
|
McConnelsville
|
|
State
|
Ohio
|
|
Post code
|
43756
|
|
Country
|
U.S.A.
|
|
Telephone
|
|
|
Fax
|
|
|
E-mail
|
|
|
World Wide Web-URL address
|
|
|
Administrative Officer Responsible for the Project
|
|
Surname
|
|
|
First name, middle name
|
|
|
Job title
|
|
|
Direct telephone
|
|
|
Direct fax
|
|
|
Direct e-mail
|
|
|
Contact Person for AIJ Activities (if different from the Administrative Officer)
|
|
Surname
|
Kaster
|
|
First name, middle name
|
Gary
|
|
Job title
|
Chair, UtiliTree
|
|
Direct telephone
|
740-962-1200
|
|
Direct fax
|
740-962-1219
|
|
Direct e-mail
|
Gilbert_G._Kaster@aep.com
|
|
Item
|
|
|
Organization
|
|
Name of organization (original language)
or
Name of individual if unaffiliated with any organization
|
Suncor Energy, Inc.
|
|
Name of organization (English)
|
(Same as above)
|
|
Acronym (original language)
|
None
|
|
Acronym (English)
|
None
|
|
Department
|
|
|
Function(s) within the AIJ project activities
|
|
|
Street
|
112 4th Avenue, SW, PO Box 38
|
|
City
|
Calgary
|
|
State
|
Alberta
|
|
Post code
|
T2P 2V5
|
|
Country
|
Canada
|
|
Telephone
|
403-269-8100
|
|
Fax
|
|
|
E-mail
|
|
|
World Wide Web-URL address
|
www.suncor.com
|
|
Administrative Officer Responsible for the Project
|
|
Surname
|
Lambert
|
|
First name, middle name
|
Gordon R.
|
|
Job title
|
Corporate Director, Sustainable Development
|
|
Direct telephone
|
403-269-8720
|
|
Direct fax
|
403-269-6223
|
|
Direct e-mail
|
glambert@suncor.com
|
|
Contact Person for AIJ Activities (if different from the Administrative Officer)
|
|
Surname
|
|
|
First name, middle name
|
|
|
Job title
|
|
|
Direct telephone
|
|
|
Direct fax
|
|
|
Direct e-mail
|
|
-
5. Description of AIJ project activities
|
Item
|
|
|
Type of Project
|
|
Sector(s)
|
Land-use change and forestry
|
|
Primary activity(ies)
|
Forest preservation, sustainable harvesting, reduced impact logging, silviculture, fire management,
manufacture of durable wood products
|
|
Project Location
|
|
Country
|
Belize
|
|
Exact location (city, state, region)
|
In and adjacent to the eastern portion of the Rio Bravo Conservation and Management Area (RBCMA) in
northwest Belize
|
|
Key Dates and Current Stage of Project
|
|
Project starting date (month/year)
|
January 1995(a)
|
|
Project ending date (month/year)
|
October 2037
|
|
Project lifetime (years)
|
42
|
|
Current stage of project
|
In progress
|
|
General Project Description and Technical Data
|
|
This project combines land acquisition and a sustainable forestry program to achieve carbon dioxide
mitigation. The objective of the project is to demonstrate an optimal balance between cost-effective carbon
sequestration, economically sustainable forest yield, and environmental protection. The project is located
in and adjacent to the eastern portion of the RBCMA, which comprises about 104,892 hectares (ha) of land in
northwest Belize. In the west, the RBCMA extends along the Guatemalan frontier and is contiguous with the
Rio Azul National Park in the Maya Biosphere Reserve. The RBCMA is separated from Mexico to the north by 5
km.
The project has two components: (A) purchase of a parcel of endangered forest land, and (B) development of
a sustainable forestry management program. Under Component A of the project, a 5,602-ha parcel of
endangered forest land has been purchased to protect it from conversion to farmland. Component B will
establish and implement an economically sustainable forest management program on the purchased land and the
eastern portion of the RBCMA (a combined total of approximately 49,985 ha) to increase the level and rate
of carbon sequestration on these lands. This program will include sustainable logging and pine stocking
enhancement, and will provide active protection against incursion and uncontrolled fire by substituting
controlled burns for annual wild fires. The remaining RBCMA lands will be left undisturbed for conservation
and research purposes. These lands will be managed as protected forest, as will those portions of land
under Component B that are designated for preservation. The biomass characteristics of the project land as
well as land management and socioeconomic factors will be monitored to measure and verify project results.
A second phase of the project added 7707 ha of threatened land to the existing purchases under component A,
and the new land will be protected under component B with improved measures based on the experience derived
from the first phase. Among the improvements will be identification and appropriate protection of areas
with high biodiversity value or with other constraints on extractive use.
|
-
(a) The project was officially accepted by the USIJI Secretariat on February 3, 1995. However, net
project carbon benefits are calculated for the full year in 1995 because a forestry protection regime
was established on the land purchased and/or managed by the project before 1995.
|
|
Methodology for Calculating Cost Data
|
|
In the initial proposal, the project developer provided a preliminary cost estimate of US$2.5 million for
implementation of this project, and reported that the period of investment would be ten years, after which
the project would be self-sufficient. As of this writing, the cost estimate for project implementation,
including partial recovery of project development costs, had increased to US$2.6 million. The second phase
of the project is expected to cost an additional $3.0 million, including land acquisition ($2.1 million)
and management actions ($0.9 million).
The cost of project implementation totaled US$2,441,000 between the project’s inception in 1995 and
March 1999.
|
-
(b) Cost data–Project development
This information is considered confidential by the developer and therefore is not available.
(c) Cost data–Project implementation
Annual implementation cost information is not yet available.
|
Year(s)
|
Item
|
Projected Amount
(US$)
|
Actual Amount(a)
(US$)
|
|
Project Costs
|
|
|
|
Land purchase first phase
|
1,300,000
|
1,285,372
|
|
Land purchase second phase
|
2,073,000
|
1,940,219
|
|
Resource Protection Endowment
|
400,000
|
410,000
|
|
Internal Verification
|
140,000
|
18,910
|
|
Project field management
|
476,000
|
398,997
|
|
Actions
|
448,000
|
91,958
|
|
Internal monitoring
|
150,000
|
44,592
|
|
Training/Outreach
|
60,000
|
8,292
|
|
Project infrastructure
|
140,000
|
121,718
|
|
TNC financial management
|
380,000
|
157,519
|
|
PfB Administration
|
90,000
|
|
|
Partial recovery of development costs
|
0
|
|
|
Subtotal
|
5,657,000
|
4,477,577
|
|
Project Revenues
|
|
|
|
None.
|
|
|
|
Subtotal
|
|
|
|
Net Project Cost (Project Costs-Project Revenues)
|
NA
|
NA
|
|
(a) Current as of June 1999.
|
7. Monitoring and verification of AIJ project activities and results
|
Item
|
|
|
Party(ies) that will be monitoring project activities
|
Winrock International, Programme for Belize
|
|
Party(ies) that will be externally verifying project results
|
This information is not yet available.
|
|
Date when the monitoring plan became (or will become) operational (month/year)
|
February 1996
|
|
Types of data that will be collected
|
Above- and belowground woody and herbaceous biomass carbon content (including measurement of biomass
density of lesser-known species groups—palms and swamp thicket woody species), litter and necromass
carbon content, soil organic carbon content, damage (and subsequent recovery) per harvested tree,
destination of harvested biomass and wood waste, leakage of project benefits, area of burned land, and
other gross changes in land cover, land use, and land management.
|
|
Description of Monitoring and Verification Activities and Schedule for Implementation
|
|
The monitoring protocol was developed in collaboration with Winrock International. Winrock International
has trained PfB staff to conduct the monitoring activities, and will internally verify the project results.
The first monitoring activity, which began in February 1996, consisted of a project baseline carbon
inventory on Component A land. The sampling design consisted of stratified systematic sampling of permanent
sample plots. The strata were defined by vegetation type as determined from satellite images, topographic
maps, and observation of vegetation and soils. Strata areas were determined using MapInfo (versions 3.0 and
4.0) and the PfB’s Geographic Information System (ArcInfo/ArcView). To determine carbon stocks under
the reference case, it was assumed maize, beans, and rain-fed rice would be planted on deforested land, and
that the only permanent carbon pool would lie in the soils. Nearby agricultural lands were used to
represent the reference case. Monitoring of permanent sample plots was scheduled to take place in years 3,
5, 7, and 10 with existing project funding. The first remeasurement (Year 3) was conducted from February to
April 1998. All monitoring will be conducted during the same season in each year.
For Component B land, the monitoring protocol compares the impacts of sustainable harvesting, silviculture,
and regeneration techniques (the project scenario) against the impacts of traditional harvesting practices
(the reference scenario). Component B monitoring in hardwood forest was initiated in July 1997. This
monitoring will continue as the various harvesting and silviculture techniques are implemented. Prevailing
logging practices in a nearby district at the time of project setup were used to represent the reference
case. Permanent sample plots were established for monitoring Component B land. Future sampling rates are
yet to be determined.
For both Component A and Component B, data are being collected on aboveground biomass and necromass,
estimated belowground biomass, and soil carbon. For Component B, the amount of damage per harvested tree
(e.g., the road, skid trail, and log landing areas and the volume of coarse woody debris), the destination
of harvested biomass (e.g., the proportion of extracted timber in durable products and the fossil-fuel
substitution by wood waste), and the impact of fire suppression activities (e.g., actual area burned in a
fire event that was suppressed by PfB crews, and estimated amount of land that would have been burned in
the absence of fire suppression activities) are also being assessed.
|
|
The project implementer (PfB) has obtained Smartwood and Woodmark certification under the Forest
Stewardship Council guidelines for the timber harvesting regime and other forest management practices.
Achieving such certification demonstrated that the project meets internationally recognized standards for
sustainable management of forest resources.
A protocol has also been developed to identify and monitor forms of potential leakage of project benefits.
This protocol focuses on identifying leakage issues that are specific to the project, measurable, and
actually occurring, and that have the potential to affect GHG emission benefits by 20% or more.
Land-use change over the zone of secondary project impacts has been tracked from a historical reference
point of 1968 using air photography, LANDSAT, Spot, and AIRSAR. This assessment will be updated regularly
as imagery becomes available through the Belize Ministry of Natural Resources.
The results of monitoring activities are reviewed by the Project Board and the Project Advisory Panel. All
project reports and data are available for external verification.
|
|
Item
|
|
|
Please check one of the following.
|
This report is a first report.
Or
This report is an intermediate report.
Or
This report is a final report.
|
|
Please check one of the following:
|
This report is a joint report. Letter(s) of approval of this report from the designated national authority
of the other Party(ies) involved in the activity is(are) attached in Section J, Annex.
Or
This report is a separate report.
|
|
Additional comments (if any):
|
|
|
Compatibility with Economic Development and Socioeconomic and Environmental Priorities
|
|
In his letter to the U.S. Department of State, the Foreign Minister of Belize noted that the Belizean
Government considers the project to be "a significant step in [the] direction" of the
Government’s environmental and economic development goals.
|
-
D. Environmental, social/cultural, and economic impacts of the AIJ project
|
Non-Greenhouse-Gas Environmental Impacts of the Project
|
|
The project was designed to have positive impacts on the area’s biodiversity, wildlife habitat, and
soil stability. The project will secure a habitat for a wide range of species, including nine mammals
listed on CITES Appendix 1 or classed as threatened under the U.S. Endangered Species Act, and over 341
bird species. The project will also maintain the integrity of the biodiversity in the RBCMA by promoting
the regeneration of a diverse range of native flora species. In addition, the planned sustainable forestry
regime, pine forest management activities, and Bajo scrub preservation will increase the amount of ground
cover and further reduce soil erosion.
The reduction in the availability of new farm land resulting from the land purchases in Component A may
trigger an increased use of fertilizers, pesticides and fungicides, which are known to have negative
impacts on water quality, as farmers seek to improve the productivity of available lands. However, it is
also likely that the project will have a positive effect on water quality by promoting a shift in land-use
patterns from the current high-input mechanized farming practices to more sustainable land uses (e.g.,
sustainable forestry). Significant increases in air pollution resulting from manufacturing durable wood
products are not anticipated. Increases in forest cover and subsequent reductions in ambient air
temperatures are expected to reduce the formation of ground-level ozone.
To reduce the environmental impact of project implementation, the Hillbank field station was equipped with
a solar power-generating system and a composting toilet. The project’s environmental impacts are
being monitored on an ongoing basis, and mitigation plans will be developed if any adverse affects are
identified.
|
|
Social/Cultural Impacts of the Project
|
|
The carbon sequestration activities under Component B are being integrated into the management regime for
the broader RBCMA, which includes the protection of ancient Mayan archaeological sites.
|
|
Economic Impacts of the Project
|
|
The forest management regime developed as part of the project enhances the commercial value of the forest
and regeneration of valuable timber, and helps to ensure that the forest resources are used in a
sustainable manner.
The RBCMA sustainable forestry project is labor-intensive and, thus, is improving employment in the
immediate region and adding new technical capabilities to the area’s labor market. A policy of
preference for hiring from local communities is being followed for all field posts and contract work.
The sustainable forestry program attempts to create an economically viable commercial model that
demonstrates that shifting land-use practices either from extensive agriculture to forestry, or from
unsustainable logging practices to sustainable forestry, can be economically beneficial. Once developed and
tested, the sustainable forestry management regime will be extended to benefit, both technically and
economically, a network of community groups surrounding the RBCMA.
|
-
E. Greenhouse gas impacts of the AIJ project
1. Scenario description
|
Item
|
|
|
Site Designation
|
|
Site number (order of presentation in this report)
|
1 of 2
|
|
Site name/designation
|
Component A
|
|
Project sector
|
Land-use change and forestry
|
|
Reference Scenario
|
|
Primary activity(ies)
|
Deforestation, conversion to agricultural land
|
|
Has the reference scenario changed since the last report? (If yes, explain any changes below.)
|
Yes
No
This is the first project report.
|
|
Description:
After the first report was submitted in 1996, the area of Component A land was re-estimated due to the
identification of anomalies between the areas on land titles and the actual ground areas. As indicated in
the first report, Component A was anticipated to involve the purchase of 6,014 ha of forest area,
consisting of 4,791 ha of broadleaf forest, 1,118 ha Bajo (seasonally inundated scrub), and 105 ha of
swamp. Without the project, 5,909 ha of forest area within the 6,014 ha of land purchased under Component A
of the project were expected to be deforested and converted to agricultural lands within five years; the
remaining 105 hectares of Component A were expected to remain herbaceous swamp and open water.
Based on a ground survey and GIS measurements, the actual area of Component A land is estimated to be 5,602
ha, of which 4,247 ha consist of broadleaf forest, 334 ha consist of upland forest that was burned through
in June 1995,(a) 923 ha consist of Bajo, and 98 ha consist of herbaceous swamp and open water.
Without the project, 5,504 ha were estimated to be deforested and converted to agricultural lands within
five years; the remaining 98 hectares were expected to remain herbaceous swamp and open water.
The second phase acquisition consists of 2311 ha of high forest suitable for timber offtake, 2276 ha not
suitable for timber offtake (protected forest), 2568 ha of pine savannah, and 551 ha of wetlands. In the
reference scenario, the stable soil carbon in the 4587 ha of forest land would be reduced from 298.3 tonnes
carbon per ha to 85 tonnes carbon per ha by agricultural conversion over an assumed period of five years.
|
|
Predicted Project Scenario
|
|
Primary activity(ies)
|
Forest preservation, silviculture, fire management, sustainable harvesting, reduced impact logging,
manufacture of durable wood products
|
|
Description:
Once the Component A land had been purchased, it was to be placed under the sustainable forestry management
regime established as part of Component B (see site description for Component B below). As a result, this
5,602 ha parcel of land was expected to accrue carbon benefits from both Component A (preservation) and
Component B (sustainable forestry) of the project. In order to simplify overall calculations, carbon
benefits associated with both the purchase of the 5,602 ha parcel of land, and the subsequent
implementation of the sustainable forestry management regime on this parcel of land, were to be calculated
as Component A carbon benefits. As a result of the second phase acquisition, agricultural conversion would
not occur, preserving soil carbon at the 298.3 tonnes per ha level and preventing the loss of 978,407
tonnes of carbon ultimately to the atmosphere. This amounts to 195,681 tonnes carbon (717,497 tonnes CO2)
per year.
|
|
Actual Project
|
|
Primary activity(ies)
|
Forest preservation, silviculture, fire management
|
|
Description:
The purchase of the first installment of Component A land (5,602 ha) was completed in December 1995. The
purchase of the second installment of Component A land (7,707 ha) was completed in August 1998. These areas
were managed and protected by the PfB during the year prior to purchase. As a result of the land purchase
and management efforts, no Component A land was deforested for conversion to agriculture from January 1995
through June 1999.
|
-
(a) This hardwood forest fire, which occurred under intense drought conditions, took place after PfB
had assumed management of the land but before the Comprehensive Agreement initiating the project had
become effective, before the Component A land had been purchased by PfB, and before the baseline carbon
assessment was conducted.
|
|
Item
|
|
|
Site Description
|
|
Site number (order of presentation in this report)
|
2 of 2
|
|
Site name/designation
|
Component B
|
|
Project sector
|
Land-use change and forestry
|
|
Reference Scenario
|
|
Primary activity(ies)
|
Unsustainable harvesting, uncontrolled burning of pine savannahs
|
|
Has the reference scenario changed since the last report? (If yes, explain any changes below.)
|
Yes
No
This is the first project report.
|
|
Description:
After the first USIJI report was submitted in 1996, the area of Component B land was re-estimated. As
indicated in the first USIJI report, the Component B land originally was estimated to consist of 44,529 ha
that were additional to those in Component A. Based on the results of a ground survey and GIS measurements,
the actual area of Component B land (that is additional to Component A) was estimated to be 46,406 ha.
These results were presented in the 1997 USIJI report. However, the developer reports that based on the
advice of the Commissioner of Lands, 2,023 ha will be returned to the vendor, and the area of Component B
therefore will be 44,383 ha (= 46,406 ha – 2,023 ha).
In the reference scenario, the developer makes the conservative assumption that carbon stocks on Component
B land would remain constant in the absence of the project. Since it is possible that in the absence of the
project, some or all of the Component B lands would be subject to unsustainable harvesting—which
would cause the decline of current carbon stocks in the already degraded broadleaf forest area—as
well as uncontrolled burning of pine savannas, this assumption may lead to an underestimation of project
benefits.
|
|
Predicted Project Scenario
|
|
Primary activity(ies)
|
Forest preservation, silviculture, fire management, sustainable harvesting, reduced impact logging,
manufacture of durable wood products
|
|
Description:
In the original proposal, the combined land in Component A and Component B was expected to total 50,543 ha.
Of this total, 11,398 ha were anticipated to be managed as a conservation area consisting of 3,493 ha
broadleaf, 1,815 ha swamp forest, and 6,090 ha of Bajo. In addition, a sustainable logging program was to
be established on 25,866 ha of broadleaf forest. A fire control regime was initially to be applied to 2,500
ha of pine forest, and eventually to be expanded to 10,010 ha of pine forest. The remaining 3,269 ha were
to consist of herbaceous swamp and open water.
Using the revised land area data based on the ground survey and GIS analysis, the combined land in
Component A and Component B of the project was found to total 52,008 ha. As discussed above, this anomaly
between the two estimates was resolved on the advice of the Commissioner of Lands. The land has been
resurveyed, and 2,023 ha of Component B land will be returned to the vendor. Therefore, the total land area
managed under Components A and B will be 49,985 ha, and the land area managed under only Component B will
be 44,383 ha.
A portion of this land was anticipated to be managed as a conservation area, and a portion to be used for a
sustainable logging program. A fire control regime was also to be implemented. The results of experiments
in tree regeneration, sustainable harvesting, and reduced impact logging techniques were to be used to
determine the type and extent of these activities on Component B land during the project lifetime.
In the 7707 ha second phase addition, sustainable timber practices on 2311 ha will have no net carbon
impact, while total carbon contained in the 2276 ha of protected forest will increase from 296.3 tonnes
carbon per ha to 345.1 tonnes carbon per ha over the 40 year project life, amounting to 2,662.9 tonnes
carbon per year for the new area. Pine regeneration measures on the 2568 ha of pine savannah should
increase total carbon from 3.5 tonnes carbon per ha to 102.8 tonnes carbon per ha, amounting to an
additional 1241 tonnes carbon per year. The total impact of Component B for the second phase addition will
be 3904 tonnes carbon per year for 40 years.
|
|
Actual Project
|
|
Primary activity(ies)
|
Forest preservation, silviculture, fire management, experimental use of sustainable harvesting, assisted
regeneration, and reduced impact logging techniques
|
|
Description:
In 1996, the project developers initiated a series of "patch cut" experiments to test methods of
mahogany regeneration, conducted experiments on sustainable harvesting and reduced impact logging, and
initiated a stock survey. The fire control regime was also implemented in 1996. In 1997 and 1998, the
experimental sustainable harvesting was raised to operational scale and certified under the Forest
Stewardship guidelines. Tracking of timber through processing was also implemented. Programs initiated in
1996 were maintained and expanded in scope during 1997 and 1998.
|
-
2. GHG emission/sequestration calculation methodology
|
GHG Emission/Sequestration Calculation Methodology
|
|
Site number
|
1 of 2
|
|
Project sector
|
Land-use change and forestry
|
|
Description of Calculation Methodology for the Reference Scenario
|
|
In order to simplify overall calculations, carbon benefits associated with both the purchase of the 5,602
ha parcel of land in Component A, and the subsequent implementation of the sustainable forestry management
regime on this parcel of land, are calculated as Component A carbon benefits. The project developer
indicated that all of the Component A land (5,602 ha) was purchased by the end of December 1995. Because a
forestry protection regime was established on the land purchased by the project before 1995, reference case
and project scenario emissions, and net project carbon benefits, are calculated for the full year in 1995.
The proposal assumed that without the project, 5,909 ha of forest area within the 6,014 ha of land expected
to be purchased under Component A of the project would be deforested and converted to agricultural lands
within five years. The proposal further assumed a linear rate of conversion. The initial carbon stocks on
Component A land were estimated to be 768,480 metric tonnes (t) C, based on relevant literature rather than
site-specific stock surveys. For the first five years of the project, the estimates of carbon stocks for
any given year accounted for: 1) the loss of initial (i.e., as of the end of 1994) biomass carbon stocks on
the parcel of land deforested in that year; 2) the loss of any additional carbon accumulated on that parcel
as a result of biomass growth prior to deforestation; 3) the accumulation of new carbon stocks from biomass
growth on parcels not yet deforested; and 4) the accumulation of carbon stocks in crops grown on deforested
parcels. Annual carbon emissions in the reference case were calculated by subtracting the carbon stock in
the year considered from the carbon stock in the previous year. The proposal estimated that net emissions
of 738,935 t C (= 2,709,428 t CO2) would be generated under the reference scenario over a
five-year period.
Based on on-site assessments, the land area of Component A was determined to be 5,602 ha, of which 5,504 ha
were anticipated to be deforested at a linear rate over a five-year period. The developers conducted a
biomass stock survey and sampled the soil of the Component A land, and applied biomass and soil carbon
equations to determine the carbon content of the above- and belowground biomass and the soil. The
developers determined that current carbon stocks on Component A land total 1,568,907 t C.
To develop site-specific estimates of carbon stocks under the revised reference case, the developers
assumed that maize, beans, and rain-fed rice would be planted on deforested land, and collected data on the
carbon stocks on agricultural land adjacent to the project site. The developers assumed that soil carbon
was the only stable carbon pool in cultivated fields, and did not assess the carbon content of arable
crops. The carbon stocks on an area of agricultural land equivalent to the area of Component A were
estimated to be 467,815 t C.
The difference between the carbon stocks on the Component A land and carbon stocks on the agricultural land
used to represent the end-point of the reference case was used as a measure of cumulative carbon emissions
under the reference case. Total emissions under the reference case were therefore 1,101,093 t C (=
1,568,907 t C – 467,815 t C). Annual carbon emissions over a five-year period were therefore 220,219
t C/yr (= 1,101,093 t C ÷ 5 years). To convert t C to t CO2, the tonnes of annual carbon
emissions were multiplied by the ratio of 44 t CO2/12 t C.
|
|
A similar approach was used to calculate the emissions for the second phase acquisition. In this case, the
stable soil carbon in the 4587 ha of forest land would be reduced from 298.3 tonnes carbon per ha to 85
tonnes carbon per ha by agricultural conversion over an assumed period of five years beginning in 1997.
Annual carbon emissions for this period would thus be 195,681 tonnes of carbon (717,563 tonnes CO2).
(Numbers as shown in the following tables may not sum to totals due to rounding.)(a)
|
|
Description of Calculation Methodology for the Project Scenario
|
|
As discussed above, in the proposal, the initial carbon stock of Component A forest land was estimated to
be 768,480 t C on an area of 5,909 ha. The proposal indicated that with the project, 0.96 t C/ha-yr was
expected to be sequestered due to biomass growth. (The figure of 0.96 t C/ha-yr was a weighted average
based on the biomass growth rates of broadleaf forest, Bajo, and herbaceous swamp and open water area. As
indicated by the project developer, biomass growth on the project area was only anticipated to occur during
the first five years of the project.) Average annual carbon stocks in the first five years of the project
were determined by adding the average annual biomass growth to the carbon stock in the previous year.
Carbon stocks were expected to remain constant after 2000 because biomass growth on Component A forest was
anticipated to cease in that year. Annual carbon sequestration in the project scenario was calculated by
subtracting the carbon stock in a given year from the carbon stock in the previous year. The total carbon
sequestration resulting from the project scenario on Component A land over a five-year period was
calculated to be 28,745 t C (=105,398 t CO2).
As discussed above, the developers determined that the current carbon stocks on 5,504 ha of Component A
land total 1,568,907 t C. Under the project scenario, these carbon stocks were expected to remain constant
over a five-year period. Therefore, zero carbon emissions/sequestration were projected to occur on
Component A land under the project. However, the developers acknowledged that some growth increment was
likely to occur on Component A land during the five-year period, and that some sustainable timber
harvesting could occur on this land as well. The developers planned to account for these impacts by
monitoring the changes in carbon stocks on Component A land on a regular basis.
|
|
Description of Calculation Methodology for the Actual Project
|
|
For the first three years of the project (1995 through 1997), the project developers reported that zero
deforestation had occurred on Component A land. Therefore, carbon stocks on Component A land remained
unchanged and zero carbon emissions or sequestration were reported for those years. Incremental growth in
this area during these years will be factored in following each remeasurement of the permanent plots. The
results of the 2000 remeasurement, when analyzed, will be accounted for in the 2001 USIJI report.
|
|
|
|
GHG Emission/Sequestration Calculation Methodology
|
|
Site number
|
2 of 2
|
|
Project sector
|
Land-use change and forestry
|
|
Description of Calculation Methodology for the Reference Scenario
|
|
In the proposal, Component B of the project was projected to involve the implementation of a sustainable
forestry management regime on 50,543 ha of forest area, including the 6,014 ha of land purchased under
Component A of the project. In order to simplify overall carbon benefits calculations, carbon benefits
associated with both the purchase of the 6,014 ha parcel of land, and the implementation of the Component B
sustainable forestry management regime on this parcel of land, were calculated as Component A carbon
benefits. Component B carbon benefits were calculated as the benefits accrued from the implementation of
the sustainable forestry management regime on 44,529 ha (= 50,543 ha - 6,014 ha) of land.
The proposal estimated that the initial carbon stock on the area under Component B was 4,199,218 t C.
Without the project, the current carbon stock was anticipated to remain constant, a conservative
assumption. Therefore, zero carbon emissions or sequestration were anticipated to occur under the reference
scenario.
|
|
Description of Calculation Methodology for the Project Scenario
|
|
The proposal estimated that over the course of the project, biomass carbon stocks would increase from
4,199,218 t C to 4,741,032 t C on the project area of 44,529 ha, leading to a total stock increase of
541,814 t C. These estimated carbon stock increases were described as conservative and were based on
average annual biomass accumulation rates, analysis of the impacts of sustainable harvesting and low-impact
logging approaches within the region (e.g., strip-cutting, heavy selective thinning, and block cutting),
and analysis of fire protection practices developed and tested on the southern coastal plains of Belize.
Thus, on average, the carbon stock was expected to increase by 13,545 t C/yr (= 541,814 t C/40 years).
Average annual carbon sequestration in the project scenario was calculated by subtracting the carbon stock
in the year considered from the carbon stock in the previous year, and averaged 13,545 t C/yr (= 49,666 t
CO2/yr). Although the manufacture of durable wood products was included as part of the
sustainable harvesting activities under Components A and B, the associated carbon benefits were not
included in the GHG benefit estimation process in the proposal. Therefore, the GHG benefits resulting from
the project were underestimated.
In the 7707 ha second phase addition, sustainable timber practices on 2311 ha will have no net carbon
impact, while total carbon contained in the 2276 ha of protected forest will increase from 296.3 tonnes
carbon per ha to 345.1 tonnes carbon per ha over the 40 year project life, amounting to 2,662.9 tonnes
carbon per year for the new area. Pine regeneration measures on the 2568 ha of pine savannah should
increase total carbon from 3.5 tonnes carbon per ha to 102.8 tonnes carbon per ha, amounting to an
additional 1241 tonnes carbon per year. The total impact of Component B for the second phase addition will
be 3904 tonnes carbon (14,316 tonnes CO2) per year for 40 years.
The project developers planned to revise the project scenario based on the results of a site-specific
biomass stock survey and experiments involving tree regeneration, sustainable harvesting, and reduced
impact logging. These activities have not yet been concluded, and no additional information is available on
the revised project scenario. Therefore, the emissions estimates from the proposal are presented in the
following tables.
|
|
Description of Calculation Methodology for the Actual Project
|
|
Sustainable harvesting, including reduced impact logging methods, was initiated over 120 ha in 1997 (Year
3), and increased to 350 ha in 1998 (Year 4). The experiments on tree regeneration were maintained and
incorporated in the sustainable harvesting regime. Component B monitoring was established in late 1997 and
completed in early 1998. The results are under analysis. No large-scale harvesting operations took place in
the first two years of the project (1995 and 1996). Destruction of biomass and its subsequent regrowth as a
result of the experiments were determined not to be significant sources of net carbon emissions or
sequestration in the first two project years, and zero emissions or sequestration are reported. Pending the
results of the Component B monitoring, zero emissions are reported for 1995 through 1997, but these
estimates will be adjusted as the information is received.
|

|
Projected Greenhouse Gas Benefits by Project Site (Continued)
(Tonnes, Full Molecular Weight Basis)
|
|
Site Number: 1 of 2
|
|
Reference Scenario
Emissions
|
Project Scenario
Emissions
|
Net GHG Benefits
(Reference Scenario -
Project Scenario)
|
Cumulative GHG Benefits
(Reference Scenario -
Project Scenario)
|
|
Year
|
CO2
|
CH4
|
N2O
|
CO2
|
CH4
|
N2O
|
CO2
|
CH4
|
N2O
|
CO2-
Equivalent
|
CO2
|
CH4
|
N2O
|
CO2-
Equivalent
|
|
26
|
0
|
|
|
0
|
|
|
0
|
|
|
0
|
7,624,833
|
|
|
7,624,833
|
|
27
|
0
|
|
|
0
|
|
|
0
|
|
|
0
|
7,624,833
|
|
|
7,624,833
|
|
28
|
0
|
|
|
0
|
|
|
0
|
|
|
0
|
7,624,833
|
|
|
7,624,833
|
|
29
|
0
|
|
|
0
|
|
|
0
|
|
|
0
|
7,624,833
|
|
|
7,624,833
|
|
30
|
0
|
|
|
0
|
|
|
0
|
|
|
0
|
7,624,833
|
|
|
7,624,833
|
|
31
|
0
|
|
|
0
|
|
|
0
|
|
|
0
|
7,624,833
|
|
|
7,624,833
|
|
32
|
0
|
|
|
0
|
|
|
0
|
|
|
0
|
7,624,833
|
|
|
7,624,833
|
|
33
|
0
|
|
|
0
|
|
|
0
|
|
|
0
|
7,624,833
|
|
|
7,624,833
|
|
34
|
0
|
|
|
0
|
|
|
0
|
|
|
0
|
7,624,833
|
|
|
7,624,833
|
|
35
|
0
|
|
|
0
|
|
|
0
|
|
|
0
|
7,624,833
|
|
|
7,624,833
|
|
36
|
0
|
|
|
0
|
|
|
0
|
|
|
0
|
7,624,833
|
|
|
7,624,833
|
|
37
|
0
|
|
|
0
|
|
|
0
|
|
|
0
|
7,624,833
|
|
|
7,624,833
|
|
38
|
0
|
|
|
0
|
|
|
0
|
|
|
0
|
7,624,833
|
|
|
7,624,833
|
|
39
|
0
|
|
|
0
|
|
|
0
|
|
|
0
|
7,624,833
|
|
|
7,624,833
|
|
40
|
0
|
|
|
0
|
|
|
0
|
|
|
0
|
7,624,833
|
|
|
7,624,833
|
|
41
|
0
|
|
|
0
|
|
|
0
|
|
|
0
|
7,624,833
|
|
|
7,624,833
|
|
42
|
0
|
|
|
0
|
|
|
0
|
|
|
0
|
7,624,833
|
|
|
7,624,833
|
|
Total
|
7,624,833
|
|
|
0
|
|
|
7,624,833
|
|
|
7,624,833
|
7,624,833
|
|
|
7,624,833
|
|
Projected Greenhouse Gas Benefits by Project Site
(Tonnes, Full Molecular Weight Basis)
|
|
Site Number: 2 of 2
|
|
Sector(s): Land use change and forestry
|
|
Project Activity(ies): Forest preservation, sustainable harvesting, reduced impact logging,
silviculture, fire management, manufacture of durable wood products
|
|
Please specify: Year 1 = January 1995 to December 1995
|
|
Reference Scenario
Emissions
|
Project Scenario
Emissions
|
Net GHG Benefits
(Reference Scenario -
Project Scenario)
|
Cumulative GHG Benefits
(Reference Scenario -
Project Scenario)
|
|
Year
|
CO2
|
CH4
|
N2O
|
CO2
|
CH4
|
N2O
|
CO2
|
CH4
|
N2O
|
CO2-
Equivalent
|
CO2
|
CH4
|
N2O
|
CO2-
Equivalent
|
|
1
|
0
|
|
|
-49,666
|
|
|
49,666
|
|
|
49,666
|
49,666
|
|
|
49,666
|
|
2
|
0
|
|
|
-49,666
|
|
|
49,666
|
|
|
49,666
|
99,333
|
|
|
99,333
|
|
3
|
0
|
|
|
-63,982
|
|
|
63,982
|
|
|
63,982
|
163,314
|
|
|
163,314
|
|
4
|
0
|
|
|
-63,982
|
|
|
63,982
|
|
|
63,982
|
227,296
|
|
|
227,296
|
|
5
|
0
|
|
|
-63,982
|
|
|
63,982
|
|
|
63,982
|
291,278
|
|
|
291,278
|
|
6
|
0
|
|
|
-63,982
|
|
|
63,982
|
|
|
63,982
|
355,259
|
|
|
355,259
|
|
7
|
0
|
|
|
-63,982
|
|
|
63,982
|
|
|
63,982
|
419,241
|
|
|
419,241
|
|
8
|
0
|
|
|
-63,982
|
|
|
63,982
|
|
|
63,982
|
483,223
|
|
|
483,223
|
|
9
|
0
|
|
|
-63,982
|
|
|
63,982
|
|
|
63,982
|
547,204
|
|
|
547,204
|
|
10
|
0
|
|
|
-63,982
|
|
|
63,982
|
|
|
63,982
|
611,186
|
|
|
611,186
|
|
11
|
0
|
|
|
-63,982
|
|
|
63,982
|
|
|
63,982
|
675,168
|
|
|
675,168
|
|
12
|
0
|
|
|
-63,982
|
|
|
63,982
|
|
|
63,982
|
739,149
|
|
|
739,149
|
|
13
|
0
|
|
|
-63,982
|
|
|
63,982
|
|
|
63,982
|
803,131
|
|
|
803,131
|
|
14
|
0
|
|
|
-63,982
|
|
|
63,982
|
|
|
63,982
|
867,113
|
|
|
867,113
|
|
15
|
0
|
|
|
-63,982
|
|
|
63,982
|
|
|
63,982
|
931,094
|
|
|
931,094
|
|
16
|
0
|
|
|
-63,982
|
|
|
63,982
|
|
|
63,982
|
995,076
|
|
|
995,076
|
|
17
|
0
|
|
|
-63,982
|
|
|
63,982
|
|
|
63,982
|
1,059,058
|
|
|
1,059,058
|
|
18
|
0
|
|
|
-63,982
|
|
|
63,982
|
|
|
63,982
|
1,123,040
|
|
|
1,123,040
|
|
19
|
0
|
|
|
-63,982
|
|
|
63,982
|
|
|
63,982
|
1,187,021
|
|
|
1,187,021
|
|
20
|
0
|
|
|
-63,982
|
|
|
63,982
|
|
|
63,982
|
1,251,003
|
|
|
1,251,003
|
|
21
|
0
|
|
|
-63,982
|
|
|
63,982
|
|
|
63,982
|
1,314,985
|
|
|
1,314,985
|
|
22
|
0
|
|
|
-63,982
|
|
|
63,982
|
|
|
63,982
|
1,378,966
|
|
|
1,378,966
|
|
23
|
0
|
|
|
-63,982
|
|
|
63,982
|
|
|
63,982
|
1,442,948
|
|
|
1,442,948
|
|
24
|
0
|
|
|
-63,982
|
|
|
63,982
|
|
|
63,982
|
1,506,930
|
|
|
1,506,930
|
|
25
|
0
|
|
|
-63,982
|
|
|
63,982
|
|
|
63,982
|
1,570,911
|
|
|
1,570,911
|
|
Projected Greenhouse Gas Benefits by Project Site (Continued)
(Tonnes, Full Molecular Weight Basis)
|
|
Site Number: 2 of 2
|
|
Reference Scenario
Emissions
|
Project Scenario
Emissions
|
Net GHG Benefits
(Reference Scenario -
Project Scenario)
|
Cumulative GHG Benefits
(Reference Scenario -
Project Scenario)
|
|
Year
|
CO2
|
CH4
|
N2O
|
CO2
|
CH4
|
N2O
|
CO2
|
CH4
|
N2O
|
CO2-
Equivalent
|
CO2
|
CH4
|
N2O
|
CO2-
Equivalent
|
|
26
|
0
|
|
|
-63,982
|
|
|
63,982
|
|
|
63,982
|
1,634,893
|
|
|
1,634,893
|
|
27
|
0
|
|
|
-63,982
|
|
|
63,982
|
|
|
63,982
|
1,698,875
|
|
|
1,698,875
|
|
28
|
0
|
|
|
-63,982
|
|
|
63,982
|
|
|
63,982
|
1,762,856
|
|
|
1,762,856
|
|
29
|
0
|
|
|
-63,982
|
|
|
63,982
|
|
|
63,982
|
1,826,838
|
|
|
1,826,838
|
|
30
|
0
|
|
|
-63,982
|
|
|
63,982
|
|
|
63,982
|
1,890,820
|
|
|
1,890,820
|
|
31
|
0
|
|
|
-63,982
|
|
|
63,982
|
|
|
63,982
|
1,954,801
|
|
|
1,954,801
|
|
32
|
0
|
|
|
-63,982
|
|
|
63,982
|
|
|
63,982
|
2,018,783
|
|
|
2,018,783
|
|
33
|
0
|
|
|
-63,982
|
|
|
63,982
|
|
|
63,982
|
2,082,765
|
|
|
2,082,765
|
|
34
|
0
|
|
|
-63,982
|
|
|
63,982
|
|
|
63,982
|
2,146,746
|
|
|
2,146,746
|
|
35
|
0
|
|
|
-63,982
|
|
|
63,982
|
|
|
63,982
|
2,210,728
|
|
|
2,210,728
|
|
36
|
0
|
|
|
-63,982
|
|
|
63,982
|
|
|
63,982
|
2,274,710
|
|
|
2,274,710
|
|
37
|
0
|
|
|
-63,982
|
|
|
63,982
|
|
|
63,982
|
2,338,691
|
|
|
2,338,691
|
|
38
|
0
|
|
|
-63,982
|
|
|
63,982
|
|
|
63,982
|
2,402,673
|
|
|
2,402,673
|
|
39
|
0
|
|
|
-63,982
|
|
|
63,982
|
|
|
63,982
|
2,466,655
|
|
|
2,466,655
|
|
40
|
0
|
|
|
-63,982
|
|
|
63,982
|
|
|
63,982
|
2,530,637
|
|
|
2,530,637
|
|
41
|
0
|
|
|
-14,315
|
|
|
14,315
|
|
|
14,315
|
2,544,952
|
|
|
2,544,952
|
|
42
|
0
|
|
|
-14,315
|
|
|
14,315
|
|
|
14,315
|
2,559,267
|
|
|
2,559,267
|
|
Total
|
0
|
|
|
-2,559,267
|
|
|
2,559,267
|
|
|
2,559,267
|
2,559,267
|
|
|
2,559,267
|
|
Projected Net Greenhouse Gas Benefits: All Project Sites
(Tonnes, Full Molecular Weight Basis)
|
|
Please specify: Year 1 = January 1995 to December 1995
|
|
Reference Scenario
Emissions
|
Project Scenario
Emissions
|
Net GHG Benefits
(Reference Scenario -
Project Scenario)
|
Cumulative GHG Benefits
(Reference Scenario -
Project Scenario)
|
|
Year
|
CO2
|
CH4
|
N2O
|
CO2
|
CH4
|
N2O
|
CO2
|
CH4
|
N2O
|
CO2-
Equivalent
|
CO2
|
CH4
|
N2O
|
CO2-
Equivalent
|
|
1
|
807,468
|
|
|
-49,666
|
|
|
857,134
|
|
|
857,134
|
857,134
|
|
|
857,134
|
|
2
|
807,468
|
|
|
-49,666
|
|
|
857,134
|
|
|
857,134
|
1,714,269
|
|
|
1,714,269
|
|
3
|
1,524,967
|
|
|
-63,982
|
|
|
1,588,948
|
|
|
1,588,948
|
3,303,217
|
|
|
3,303,217
|
|
4
|
1,524,967
|
|
|
-63,982
|
|
|
1,588,948
|
|
|
1,588,948
|
4,892,166
|
|
|
4,892,166
|
|
5
|
1,524,967
|
|
|
-63,982
|
|
|
1,588,948
|
|
|
1,588,948
|
6,481,114
|
|
|
6,481,114
|
|
6
|
717,498
|
|
|
-63,982
|
|
|
781,480
|
|
|
781,480
|
7,262,594
|
|
|
7,262,594
|
|
7
|
717,498
|
|
|
-63,982
|
|
|
781,480
|
|
|
781,480
|
8,044,074
|
|
|
8,044,074
|
|
8
|
0
|
|
|
-63,982
|
|
|
63,982
|
|
|
63,982
|
8,108,056
|
|
|
8,108,056
|
|
9
|
0
|
|
|
-63,982
|
|
|
63,982
|
|
|
63,982
|
8,172,038
|
|
|
8,172,038
|
|
10
|
0
|
|
|
-63,982
|
|
|
63,982
|
|
|
63,982
|
8,236,019
|
|
|
8,236,019
|
|
11
|
0
|
|
|
-63,982
|
|
|
63,982
|
|
|
63,982
|
8,300,001
|
|
|
8,300,001
|
|
12
|
0
|
|
|
-63,982
|
|
|
63,982
|
|
|
63,982
|
8,363,983
|
|
|
8,363,983
|
|
13
|
0
|
|
|
-63,982
|
|
|
63,982
|
|
|
63,982
|
8,427,964
|
|
|
8,427,964
|
|
14
|
0
|
|
|
-63,982
|
|
|
63,982
|
|
|
63,982
|
8,491,946
|
|
|
8,491,946
|
|
15
|
0
|
|
|
-63,982
|
|
|
63,982
|
|
|
63,982
|
8,555,928
|
|
|
8,555,928
|
|
16
|
0
|
|
|
-63,982
|
|
|
63,982
|
|
|
63,982
|
8,619,909
|
|
|
8,619,909
|
|
17
|
0
|
|
|
-63,982
|
|
|
63,982
|
|
|
63,982
|
8,683,891
|
|
|
8,683,891
|
|
18
|
0
|
|
|
-63,982
|
|
|
63,982
|
|
|
63,982
|
8,747,873
|
|
|
8,747,873
|
|
19
|
0
|
|
|
-63,982
|
|
|
63,982
|
|
|
63,982
|
8,811,855
|
|
|
8,811,855
|
|
20
|
0
|
|
|
-63,982
|
|
|
63,982
|
|
|
63,982
|
8,875,836
|
|
|
8,875,836
|
|
21
|
0
|
|
|
-63,982
|
|
|
63,982
|
|
|
63,982
|
8,939,818
|
|
|
8,939,818
|
|
22
|
0
|
|
|
-63,982
|
|
|
63,982
|
|
|
63,982
|
9,003,800
|
|
|
9,003,800
|
|
23
|
0
|
|
|
-63,982
|
|
|
63,982
|
|
|
63,982
|
9,067,781
|
|
|
9,067,781
|
|
24
|
0
|
|
|
-63,982
|
|
|
63,982
|
|
|
63,982
|
9,131,763
|
|
|
9,131,763
|
|
25
|
0
|
|
|
-63,982
|
|
|
63,982
|
|
|
63,982
|
9,195,745
|
|
|
9,195,745
|
|
Projected Net Greenhouse Gas Benefits: All Project Sites (Continued)
(Tonnes, Full Molecular Weight Basis)
|
|
Reference Scenario
Emissions
|
Project Scenario
Emissions
|
Net GHG Benefits
(Reference Scenario -
Project Scenario)
|
Cumulative GHG Benefits
(Reference Scenario -
Project Scenario)
|
|
Year
|
CO2
|
CH4
|
N2O
|
CO2
|
CH4
|
N2O
|
CO2
|
CH4
|
N2O
|
CO2-
Equivalent
|
CO2
|
CH4
|
N2O
|
CO2-
Equivalent
|
|
26
|
0
|
|
|
-63,982
|
|
|
63,982
|
|
|
63,982
|
9,259,726
|
|
|
9,259,726
|
|
27
|
0
|
|
|
-63,982
|
|
|
63,982
|
|
|
63,982
|
9,323,708
|
|
|
9,323,708
|
|
28
|
0
|
|
|
-63,982
|
|
|
63,982
|
|
|
63,982
|
9,387,690
|
|
|
9,387,690
|
|
29
|
0
|
|
|
-63,982
|
|
|
63,982
|
|
|
63,982
|
9,451,671
|
|
|
9,451,671
|
|
30
|
0
|
|
|
-63,982
|
|
|
63,982
|
|
|
63,982
|
9,515,653
|
|
|
9,515,653
|
|
31
|
0
|
|
|
-63,982
|
|
|
63,982
|
|
|
63,982
|
9,579,635
|
|
|
9,579,635
|
|
32
|
0
|
|
|
-63,982
|
|
|
63,982
|
|
|
63,982
|
9,643,616
|
|
|
9,643,616
|
|
33
|
0
|
|
|
-63,982
|
|
|
63,982
|
|
|
63,982
|
9,707,598
|
|
|
9,707,598
|
|
34
|
0
|
|
|
-63,982
|
|
|
63,982
|
|
|
63,982
|
9,771,580
|
|
|
9,771,580
|
|
35
|
0
|
|
|
-63,982
|
|
|
63,982
|
|
|
63,982
|
9,835,561
|
|
|
9,835,561
|
|
36
|
0
|
|
|
-63,982
|
|
|
63,982
|
|
|
63,982
|
9,899,543
|
|
|
9,899,543
|
|
37
|
0
|
|
|
-63,982
|
|
|
63,982
|
|
|
63,982
|
9,963,525
|
|
|
9,963,525
|
|
38
|
0
|
|
|
-63,982
|
|
|
63,982
|
|
|
63,982
|
10,027,507
|
|
|
10,027,507
|
|
39
|
0
|
|
|
-63,982
|
|
|
63,982
|
|
|
63,982
|
10,091,488
|
|
|
10,091,488
|
|
40
|
0
|
|
|
-63,982
|
|
|
63,982
|
|
|
63,982
|
10,155,470
|
|
|
10,155,470
|
|
41
|
0
|
|
|
-14,315
|
|
|
14,315
|
|
|
14,315
|
10,169,785
|
|
|
10,169,785
|
|
42
|
0
|
|
|
-14,315
|
|
|
14,315
|
|
|
14,315
|
10,184,101
|
|
|
10,184,101
|
|
Total
|
7,624,833
|
|
|
-2,559,267
|
|
|
10,184,101
|
|
|
10,184,101
|
10,184,101
|
|
|
10,184,101
|
|
Actual Greenhouse Gas Benefits by Project Site
(Tonnes, Full Molecular Weight Basis)
|
|
Site Number: 1 of 2
|
|
Sector(s): Land use change and forestry
|
|
Project Activity(ies): Forest preservation, sustainable harvesting, reduced impact logging,
silviculture, fire management, manufacture of durable wood products
|
|
Please specify: Year 1 = January 1995 to December 1995
|
|
Reference Scenario
Emissions
|
Project Scenario
Emissions
|
Net GHG Benefits
(Reference Scenario -
Project Scenario)
|
Cumulative GHG Benefits
(Reference Scenario -
Project Scenario)
|
|
Year
|
CO2
|
CH4
|
N2O
|
CO2
|
CH4
|
N2O
|
CO2
|
CH4
|
N2O
|
CO2-
Equivalent
|
CO2
|
CH4
|
N2O
|
CO2-
Equivalent
|
|
1
|
807,468
|
|
|
0
|
|
|
807,468
|
|
|
807,468
|
807,468
|
|
|
807,468
|
|
2
|
807,468
|
|
|
0
|
|
|
807,468
|
|
|
807,468
|
1,614,936
|
|
|
1,614,936
|
|
3
|
807,468
|
|
|
0
|
|
|
807,468
|
|
|
807,468
|
2,422,405
|
|
|
2,422,405
|
|
4
|
807,468
|
|
|
0
|
|
|
807,468
|
|
|
807,468
|
3,229,873
|
|
|
3,229,873
|
|
Total
|
3,229,873
|
|
|
0
|
|
|
3,229,873
|
|
|
3,229,873
|
3,229,873
|
|
|
3,229,873
|
|
Actual Greenhouse Gas Benefits by Project Site
(Tonnes, Full Molecular Weight Basis)
|
|
Site Number: 2 of 2
|
|
Sector(s): Land use change and forestry
|
|
Project Activity(ies): Forest preservation, sustainable harvesting, reduced impact logging,
silviculture, fire management, manufacture of durable wood products
|
|
Please specify: Year 1 = January 1995 to December 1995
|
|
Reference Scenario
Emissions
|
Project Scenario
Emissions
|
Net GHG Benefits
(Reference Scenario -
Project Scenario)
|
Cumulative GHG Benefits
(Reference Scenario -
Project Scenario)
|
|
Year
|
CO2
|
CH4
|
N2O
|
CO2
|
CH4
|
N2O
|
CO2
|
CH4
|
N2O
|
CO2-
Equivalent
|
CO2
|
CH4
|
N2O
|
CO2-
Equivalent
|
|
1
|
0
|
|
|
0
|
|
|
0
|
|
|
0
|
0
|
|
|
0
|
|
2
|
0
|
|
|
0
|
|
|
0
|
|
|
0
|
0
|
|
|
0
|
|
3
|
0
|
|
|
0
|
|
|
0
|
|
|
0
|
0
|
|
|
0
|
|
4
|
0
|
|
|
0
|
|
|
0
|
|
|
0
|
0
|
|
|
0
|
|
Total
|
0
|
|
|
0
|
|
|
0
|
|
|
0
|
0
|
|
|
0
|
|
Actual Greenhouse Gas Benefits: All Project Sites
(Tonnes, Full Molecular Weight Basis)
|
|
|
Please specify: Year 1 = January 1995 to December 1995
|
|
Reference Scenario
Emissions
|
Project Scenario
Emissions
|
Net GHG Benefits
(Reference Scenario -
Project Scenario)
|
Cumulative GHG Benefits
(Reference Scenario -
Project Scenario)
|
|
Year
|
CO2
|
CH4
|
N2O
|
CO2
|
CH4
|
N2O
|
CO2
|
CH4
|
N2O
|
CO2-
Equivalent
|
CO2
|
CH4
|
N2O
|
CO2-
Equivalent
|
|
1
|
807,468
|
|
|
0
|
|
|
807,468
|
|
|
807,468
|
807,468
|
|
|
807,468
|
|
2
|
807,468
|
|
|
0
|
|
|
807,468
|
|
|
807,468
|
1,614,936
|
|
|
1,614,936
|
|
3
|
807,468
|
|
|
0
|
|
|
807,468
|
|
|
807,468
|
2,422,405
|
|
|
2,422,405
|
|
4
|
807,468
|
|
|
0
|
|
|
807,468
|
|
|
807,468
|
3,229,873
|
|
|
3,229,873
|
|
Total
|
3,229,873
|
|
|
0
|
|
|
3,229,873
|
|
|
3,229,873
|
3,229,873
|
|
|
3,229,873
|
|
Indirect or Secondary GHG Impacts (Positive and Negative)
|
|
By maximizing timber values and implementing sustainable forest uses, the project reduces the threat of
leakage by providing surrounding communities with the economic incentive to reverse current land-use trends
and to maintain forest cover. A detailed assessment of the impacts of Components A and B on the surrounding
area will be conducted as information is collected from periodic monitoring.
In the initial assessment of Component A land conducted by the project developers, the following were
identified as potential indirect or secondary GHG impacts: reinvestment of funds obtained by the seller of
the project land in activities that generate GHGs, and emissions from three diesel vehicles and other
equipment used for patrols, communications, and research purposes. In the former case, the developers found
that the seller of the project land had not invested funds generated by the sale in any activities that
were unplanned prior to the sale, or in any activities that produce significant GHG emissions. In the
latter case, the project developers determined that the vehicular impacts under the project would be
equivalent to or less than those that would have occurred if the land had been converted to agriculture.
Emissions generated by the additional equipment were determined to be insignificant. The measure of
significance is 5,000 t C/yr (equivalent to 20% of the carbon benefit of approximately 1 million t C to be
generated by Component A).
The project attempts to demonstrate economically viable sustainable land uses that retain the forest cover.
In doing so the project hopes to generate revenue to support management of the area. The project aims to
promote improved forest management within the project "zone of influence," which includes
approximately 600,000 ha of forest land surrounding the Rio Bravo Conservation Area. To date, RFB has
worked with nine communities to increase awareness of and training in agroforestry practices, including the
planting of 3,000 seedlings.
|
|
Factors That Could Cause the Future Loss or Reversal of GHG Benefits
|
|
Natural disasters, particularly fire and hurricanes, could cause the future loss of GHG benefits. The use
of silviculture techniques (e.g., patch cuts for gap generation) that are required to promote the
generation of certain timber species (e.g., mahogany) could affect the timing of project benefits, delaying
the realization of these benefits until after the ending date of the project.
|
|
Strategy for Reducing the Risk of Future Loss or Reversal of GHG Benefits
|
|
The project will undertake multiple measures to ensure long-term protection of standing biomass in the
project area. The project area is included in the Resource Protection Programme for the entire RBCMA. This
broader program includes the following elements: maintenance of a ranger force, demarcation of the area and
diffusion of the rules applicable to that area, displacement of illicit activity by strategic positioning
of other activities (e.g., research, tourism, revenue-earning actions), maintenance of a public awareness
program, and creation of entrepreneurial and employment opportunities in local communities. The project
developers have implemented a Fire Management Programme to develop effective fire fighting capability and
to research the use of fire as a management tool. The project developers have also developed a contingency
plan for implementation in the event of a hurricane. This plan includes the recovery and use of valuable
fallen timber trees.
|
|
Funding Source
|
Country of Funding Source
|
Amount ($US)
|
Percent of Total Funding (%)
|
|
Wisconsin Electric Power Company
|
U.S.A.
|
|
|
|
The Nature Conservancy
|
U.S.A.
|
|
|
|
Programme for Belize
|
Belize
|
|
|
|
Total
|
|
NA
|
100
|
|
Funding Source
|
Country of Funding Source
|
Amount ($US)
|
Percent of Total Funding (%)
|
Is This Funding Assured? (Y/N)
|
|
Wisconsin Electric Power Company
|
U.S.A.
|
1,520,000
|
27
|
Y
|
|
Detroit Edison Electric
|
U.S.A.
|
520,000
|
9
|
Y
|
|
Cinergy
|
U.S.A.
|
520,000
|
9
|
Y
|
|
Pacificorp
|
U.S.A.
|
520,000
|
9
|
Y
|
|
Utilitree
|
U.S.A.
|
520,000
|
9
|
Y
|
|
Programme for Belize
|
Belize
|
1,200,000
|
22
|
Y
|
|
Suncor
|
Canada
|
400,000
|
7
|
Y
|
|
Balance
|
|
457,000
|
8
|
Y
|
|
Total
|
|
|
100
|
|
|
Current or Planned Activities to Obtain Additional Funding
|
|
All required project funding has been secured, and is assured over the ten-year investment period, after
which the projects are anticipated to become self-sustaining. However, according to the project developers,
this does not preclude additional financial contributions by existing or future financial partners for
further project development.
|
-
G. Contribution to capacity building and technology transfer
|
Contribution to Capacity Building and Technology Transfer
|
|
This project supports the institutional development of a Belizean non-governmental organization. Emphasis
is placed on developing PfB’s capability to implement all aspects of the project. This project also
directly addresses the issue of developing innovative financing mechanisms for conservation management in
Belize.
If the model developed in the RBCMA Pilot Project proves successful, the participants plan to extend the
project beyond the current project boundaries. In his letter to the U.S. Department of State communicating
the Belizean Government’s acceptance of the project, the Foreign Minister stated, "It is,
indeed, our hope that the project would serve as a model to be applied elsewhere."
|
|
Recent Project Developments
|
|
Due to the identification of anomalies between the areas on land titles and the actual ground areas, a
ground survey and GIS analysis were conducted to verify the project area. The difference between the areas
on land titles and actual ground areas, which is equivalent to an increase in project area from 50,500 to
52,008 ha, was resolved on the advice of the Commissioner of Lands. The land has been resurveyed prior to
re-registration, and 2,023 ha under Component B will be returned to the vendor.
A baseline carbon stock assessment of Component A land and of non-project land used to represent the
reference case was conducted between February 1996 and May 1997. A stock survey and other monitoring
activities were initiated on Component B land in 1997. On Component B land, patch-cut experiments were
conducted to test methods of promoting mahogany regeneration and experiments were also conducted to assess
different methods of reduced impact logging.
In 1996, the developers produced a public-service video on the project that was broadcast on local
television as part of the PfB educational outreach efforts. Also in 1996, Utilitree joined the project as a
finance provider, and acquired 50% of the shares held by WEPCO. All finance providers hold an equal share
of the offsets.
PfB has obtained Smartwood and Woodmark certification under Forest Stewardship Council guidelines for the
timber harvesting regime and other forest management practices.
A Fire Management Plan was developed and implemented. Three fires were extinguished during the 1997 dry
season.
USIJI approval was secured for the second phase land acquisition and management elements in 1998.
|
|
Technical Difficulties and Other Obstacles Encountered
|
|
No insurmountable technical difficulties have been encountered.
|
-
I. Additional information
|
Additional Information
|
|
None.
|
|
Country/Project Title
|
Name, Title, and Government Agency of the Designated National Authority
|
Date of Approval (day/month/year)
|
|
Belize/Rio Bravo Carbon Sequestration Pilot Project
|
Dean O. Barrow, Deputy Prime Minister, Minister of Foreign Affairs, Economic Development & Attorney
General
|
28 October 1994
|
2. Letters of approval of this AIJ project report
|